Original Article Techno-Economic Assessment of a Chicken-Manure-Fed Biogas Generator System in a Philippine Farm
INTRODUCTION Agricultural
waste-to-energy systems present both challenges and opportunities for
developing countries such as the Philippines. Large-scale poultry operations
generate significant quantities of chicken manure, which, if unmanaged,
decomposes anaerobically and emits methane. Methane is a greenhouse gas with a
global warming potential approximately 27–30 times greater than carbon dioxide
over a 100-year period, making it a particularly potent contributor to climate
change U.S. Environmental Protection Agency (n.d.). Converting chicken manure into biogas
therefore supports both waste mitigation and renewable energy adoption. Electricity demand
in the Philippines continues to increase annually. The Department of Energy
reported that total electricity consumption for 2024 reached 126,941 GWh Department
of Energy (Philippines) (2024). Alongside grid supply, many rural
agricultural operations still rely on diesel generators to meet their power
needs, resulting in higher operating costs and exposure to volatile fuel
prices. These challenges underscore the importance of alternative, locally
sourced renewable energy solutions. Chicken manure
offers substantial potential as a substrate for anaerobic digestion due to its
high biodegradability and organic content. Controlled digestion produces
methane-rich biogas suitable for combustion in generator sets. The system not
only stabilizes waste but also reduces uncontrolled methane emissions,
supporting broader climate objectives. This paper
evaluates the feasibility of operating a 160-kW biogas generator using chicken
manure-derived biogas in a tropical Philippine farm. Realistic, standardized
assumptions were applied to estimate biogas requirements, methane utilization,
greenhouse gas mitigation, and economic returns. The study employs an
integrated engineering and management perspective to determine the system’s
viability as a renewable energy solution for agricultural settings. MATERIALS AND METHODS Biogas Potential of Chicken Manure Chicken manure
contains high nitrogen, volatile solids, and readily biodegradable organic
material, making it a strong substrate for anaerobic digestion Gerardi
(2003), Kelleher
et al. (2002). Typical biogas yields range from
0.035–0.060 m³/kg of fresh manure, with methane concentrations of 50–65%, as
reported in both foundational and recent studies Kelleher
et al. (2002), Mozhi et
al. (2021), Al et al. (2020). These parameters confirm poultry manure as
a reliable, energy-rich feedstock suitable for farm-scale biogas-to-electricity
systems. Anaerobic Digestion Process Anaerobic
digestion (AD) is a microbiological process in which organic substrates are
decomposed in the absence of oxygen, producing methane-rich biogas and a
stabilized digestate byproduct. It is widely recognized as an effective method
for waste treatment, renewable energy generation, and greenhouse gas mitigation
Appels
et al. (2008), Metcalf
and Eddy (2014). It progresses through four sequential
stages: hydrolysis, acidogenesis, acetogenesis, and methanogenesis Meegoda
et al. (2018), Anukam
et al. (2019). Stable biogas production is supported by
mesophilic operating temperatures of approximately 35–39 °C, which encourage
optimal microbial activity for chicken manure digestion Elsayed
et al. (2024), Steiniger
et al. (2023), Nie et al. (2021). Maintaining a near-neutral pH (typically
6.8–7.4) prevents acidification and process inhibition, while appropriate
organic loading rates and hydraulic retention times promote steady methane
formation Kumar et
al. (2024), Harirchi
et al. (2022). Collectively, these parameters ensure
efficient conversion of manure into combustible biogas suitable for
generator-set applications. Site Characteristics The site is
located in a tropical Philippine region with ambient temperatures of 22–33°C
and relative humidity above 80%. These conditions are typical for Southeast
Asian poultry operations. System Description The
biogas-to-power system evaluated in this study consists of a chicken-manure-fed
anaerobic digester and a spark-ignited internal combustion generator designed
to operate solely on biogas. The generator is rated at 160 kW, suitable for
continuous electrical load operation common in agricultural facilities. Collected chicken
manure is conveyed into the digester, where controlled anaerobic conditions
convert organic matter into biogas. The produced biogas undergoes preliminary
purification, including removal of hydrogen sulfide (H₂S) and moisture
through gas scrubbers and condensate traps. This treatment preserves engine
life and ensures consistent combustion quality. The conditioned biogas is fed
to the generator with an assumed methane concentration of 55%. This value falls
within standard performance ranges reported in literature for poultry-based
biogas systems. Electrical output is converted through an integrated switchgear
system, enabling safe distribution either to farm operations or as supplemental
power for local consumption. This configuration
represents a realistic farm-scale renewable-energy installation capable of
lowering reliance on grid electricity or diesel generators. The system
description forms the basis for the techno-economic calculations presented in
this study. Computational Methods Biogas Energy Content (MJ/Nm3) LHVbiogas = CH4% ×
LHVCH4 (1) CH4% is the
methane concentration assumed at 55% LHVCH4
is the Lower Heating Value of methane (35.8 MJ/Nm3) based on its concentration
level Biogas Flow Requirement (Nm3/hr) Q = Pη × LHVbiogas (2) P is the rated
power η is the
generator efficiency assumed at 33% LHVbiogas is the
calculated Lower Heating Value of the biogas (1 kWh = 3.6 MJ) Methane Mass Flow Rate (kg CH₄/hr) ṁCH4 = Qbiogas
× CH4% × ρCH4
(3) Qbiogas is the
biogas flow rate ρCH4 is the
density of methane at normal conditions at 0.67 kg/Nm3 Annual Methane Utilization (kg CH₄/year) mCH4_annual = ṁCH4
× H (4) H is the Annual
Operating Hours (24 hrs/day × 330 days/yr) Greenhouse Gas Mitigation (tons/year) CO2eq_annual = mCH4_annual
× GWP × 1 ton/1000 kg (5) GWP is the
100-year Global Warming Potential of methane Annual Electricity Generation (kWh/year) Eannual = P
× H (6) Diesel Displacement (Liters/year) Diesel = Eannual
× SFC (7) SFC is the
specific fuel consumption of a typical diesel generator at 0.30 Liters/kWh Economic Metrics Annual Revenue or Cost Savings from Electricity (PHP/year) Revenue = E × T (8) T is the electricity tariff at PHP 13/kWh Net Annual Savings (PHP) Savings = Revenue - OPEX
(9) OPEX is the
operating expenses estimated at PHP 1,400,000.00 (Powercity data) Payback Period (months) Payback = CAPEX is the
capital costs in the generator installation at PHP 6,5000,000.00 (Powercity
data) Return on Investment (ROI) ROI = RESULTS AND DISCUSSIONS Technical Performance The biogas
generator operated consistently at its rated output of 160 kW, supported by an
estimated fuel requirement of 90 Nm³/hr. This value is directly obtained from
the energy balance in the methodology, which incorporates a generator
efficiency of 33% and a biogas lower heating value of 19.7 MJ/Nm³ derived from
a methane concentration of 55%. The conformity of these results with
established anaerobic digestion and biogas engine performance ranges suggests
that the assumed biogas quality is sufficient to sustain stable combustion and
continuous operation. Based on 7,920
operating hours per year, the system is projected to generate approximately
1.27 GWh of electricity annually. This output represents a substantial portion
of the energy demand for typical farm operations and demonstrates the system’s
capacity to replace or reduce reliance on diesel generators and grid
electricity. The calculated performance indicates that, under the given
assumptions, a chicken-manure-fed biogas generator can provide a dependable and
decentralized energy source. Environmental Impact The environmental
benefits of the system were assessed by quantifying methane utilization and the
resulting reduction in greenhouse gas emissions. Based on a biogas consumption
rate of 90 Nm³/hr and a methane fraction of 55%, the methane mass flow was calculated
at approximately 33 kg/hr using the density of methane at standard conditions.
When applied over 24 hours and 330 operational days, annual methane utilization
reaches roughly 260,000 kg. This captured methane would otherwise be released
during unmanaged manure decomposition, making its conversion to energy a direct
mitigation of agricultural methane emissions. Using the GWP100
factor of 25, the annual methane utilization corresponds to an estimated 6,500
tons of CO₂-equivalent emissions avoided. In addition to methane
mitigation, the system offsets approximately 380,000 liters of diesel annually,
based on the calculated energy output of 1.27 GWh and a typical diesel
generator specific fuel consumption of 0.30 L/kWh. The displacement of diesel
contributes further to emission reductions and reduces reliance on fossil
fuels. These results demonstrate that the system provides meaningful
environmental gains. Economic Feasibility Economic
performance was evaluated using the projected annual energy generation and the
corresponding monetary value of displaced electricity costs. With an annual
output of 1.27 GWh and an electricity tariff of PHP 13/kWh, the system yields
an estimated annual revenue or avoided cost of PHP 16.5 million. After
accounting for operating expenses of PHP 1.4 million, net annual savings amount
to approximately PHP 15.1 million. These results are grounded in the
methodology’s financial equations, which link electrical output to revenue and
operational costs, providing a clear basis for economic interpretation. The system’s
capital cost of PHP 6.5 million is recovered in an estimated 0.43 years, or
about five months, when divided by the calculated net savings. This rapid
payback period reflects the economic strength of biogas-to-power systems,
particularly in settings where electricity prices are high and organic waste is
readily available. The implied return on investment exceeds 100 percent in the
first year alone, suggesting that the technology is not only viable but
financially advantageous for agricultural operations while simultaneously
contributing to environmental sustainability. CONCLUSIONS AND RECOMMENDATIONS This study
demonstrated that a chicken-manure-fed biogas generator can operate dependably
under typical farm conditions and can provide a practical source of on-site
power when supplied with biogas of adequate quality. The assessment showed that
transforming manure-derived methane into a usable energy stream offers tangible
environmental benefits by reducing emissions associated with unmanaged waste.
In parallel, the economic evaluation indicated that the system can offset energy-related expenses of agricultural
facilities. These findings
should be interpreted within the limits of the analytical assumptions, as
actual performance may vary with site-specific manure characteristics, digester
management, and equipment maintenance practices. Nonetheless, the integrated
methodological approach used in this study illustrates how technical,
environmental, and economic indicators can collectively inform feasibility
assessments for decentralized energy systems. Future studies may
benefit from investigating how variations in manure characteristics, digester
loading strategies, and operational conditions influence biogas yield and
generator stability. More detailed field measurements such as real-time gas
composition and digester temperature profiles would help validate and refine
the assumptions used in this assessment. Exploring co-digestion or
pre-treatment techniques may also provide insight into whether enhancements in
substrate degradability can improve system performance. In addition,
evaluating long-term operational behavior through extended monitoring of
generator efficiency and component longevity would offer valuable information
about lifecycle performance and system reliability. Assessing the agronomic
value of digestate under field conditions could also identify opportunities for
circular resource use. Collectively, these avenues for further research can
help strengthen both the methodological foundation and practical application of
biogas technologies, supporting their continued development as viable renewable
energy solutions for agricultural settings. ACKNOWLEDGMENTS The authors thank
Powercity Corporation and the partner farm in Luzon for their technical
support, site collaboration, and operational data. The authors also extend
their gratitude to the graduate school professor for guidance and feedback that
shaped this technical report. REFERENCES Al-Masri, M., Bani-Hani, E., Abu-Qdais, H., and Hayajneh, M. (2020). Biogas Production from Poultry Manure Under Optimized Conditions. Bioresource Technology Reports, 12, 100577. Anukam, A., Mohammadi, A., Naqvi, M., and Granström, K. (2019). A Review of the Chemistry of Anaerobic Digestion: Methods of Accelerating and Optimizing Process Efficiency. Processes, 7(8), 504. https://doi.org/10.3390/pr7080504 Appels, L., Baeyens, J., Degrève, J., and Dewil, R. (2008). Principles and Potential of the Anaerobic Digestion of Waste-Activated Sludge. Progress in Energy and Combustion Science, 34(6), 755–781. https://doi.org/10.1016/j.pecs.2008.06.002 Department of Energy (Philippines). (2024). Summary of Electricity Consumption 2024. Elsayed, M., Mahmoud, M., Abdelkreem, M., Azab, M., and Abdelwahab, O. (2024). Enhancing Anaerobic Digestion Efficiency: Advances in Process Optimization and Microbial Performance. Energy Conversion and Management, 307, 117902. https://doi.org/10.1016/j.enconman.2024.117902 Gerardi, M. H. (2003). The Microbiology of Anaerobic Digesters. John Wiley and Sons. https://doi.org/10.1002/0471468967 Harirchi, S., Liu, D., Chen, J., Niu, Q., Zhang, L., Dou, X., Yang, Q., and Liu, Y. (2022). Microbiological Insights into Anaerobic Digestion for Biogas Production: Microbial pathways and Engineering Implications. Bioengineered, 13(3), 6072–6090. https://doi.org/10.1080/21655979.2022.2037767 Kelleher, B., Leahy, J. J., Henihan, A. M., O’Dwyer, T. F., Sutton, D., and Leahy, M. J. (2002). Advances in Poultry Manure Disposal. Bioresource Technology, 83(1), 27–36. https://doi.org/10.1016/S0960-8524(01)00133-X Kumar, S., Shrestha, R., Maharjan, S., Paudel, S., Sharma, H., Raut, B. K., and Tripathi, R. (2024). A Comprehensive Study on Anaerobic Digestion of Organic Waste: Process Mechanisms, Operational Factors, and Stability Considerations. Cleaner Engineering and Technology, 16, 100561. https://doi.org/10.1016/j.clet.2024.100561 Meegoda, J. N., Li, B., Patel, K., and Wang, L. B. (2018). A Review of the Processes, Parameters, and Optimization of Anaerobic Digestion. International Journal of Environmental Research and Public Health, 15(10), 2224. https://doi.org/10.3390/ijerph15102224 Meegoda, J. N., Li, B., Patel, K., and Wang, L. B. (2018). A Review of the Processes, Parameters, and Optimization of Anaerobic Digestion. International Journal of Environmental Research and Public Health, 15(10), 2224. https://doi.org/10.3390/ijerph15102224 Metcalf and Eddy. (2014). Wastewater Engineering: Treatment and Resource Recovery (5th ed.). McGraw-Hill Education. Mozhi, A. R., Harikumar, A., Lakshmipathy, C., Ramalakshmi, S., Maheswari, M., Thangavel, S., and Arun, A. (2021). Anaerobic Digestion of Poultry Manure and Co-Substrates: A Review. Renewable Energy, 179, 1577–1590. Nie, Y., Li, H., Xue, Y., Chen, S., Wang, Q., Zhang, X., and Liu, Y. (2021). How Temperature Regulates Anaerobic Digestion? A Review of Microbial Mechanisms and Process Stability. Renewable and Sustainable Energy Reviews, 152, 111640. https://doi.org/10.1016/j.rser.2021.111640 Steiniger, D., Tánczos, I., Pérez-Romero, A., Dörsch, P., Rebak, A., Eberl, L., García-Martín, H., and Horn, M. A. (2023). Exploring Anaerobic Digestion from Mesophilic to Thermophilic Conditions: Microbial Dynamics and Process Performance. Fermentation, 9(9), 798. https://doi.org/10.3390/fermentation9090798 U.S. Environmental Protection Agency. (n.d.). Understanding Global Warming Potentials.
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